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德国HYDRO-BIOS公司——Van Veen采泥器 0 o: g. ?% \% c1 d, E
Bottom Sampler acc. to Van Veen
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用Van Veen采泥器(抓斗式采泥器)可以从任意想要的深度进行采样。在采泥器被沉入水中过程中，两根杆被锁定，并且离得很远，采泥器的采泥口处于打开状态。当采泥器与水床接触时，闭合器被释放；当绳缆被拉紧并向上拉动采泥器时，采泥器口就会关闭。如下图：* O8 M1 ~5 c: i2 r8 ~8 W) {
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采泥器的闭合状态 采泥器的打开状态
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Van Veen采泥器(抓斗式采泥器)订购信息：
2 K3 z% F0 z! X/ C# O437 330 Van Veen采泥器3 b, [( c) F; x* k3 R
小型采泥器，表面积250cm2，不锈钢材质
+ c. j$ E: a0 w/ Z 尺寸20×30×60 cm，重量5kg# \' D3 `8 \/ i, `
437 332 Van Veen采泥器5 w3 o9 w) ]$ g' D
大型采泥器，表面积1000cm2，不锈钢材质
4 O! X9 I8 I0 T9 \+ ^9 |1 u 尺寸35×42×90 cm，重量22kg" s( H+ u U% J5 a* l, B, Q
437 333 Van Veen采泥器
5 ]/ {* D! i d3 J4 S$ | 大型采泥器，表面积1250cm2，不锈钢材质，带活动顶盖，便于样品释放) Q8 U: [5 o) t; q" v3 d
尺寸36×45×90 cm，带配重铅块，总重量35kg（无配重）/60kg（25kg配重）, C! A) T8 P% i; p0 o1 Z# g. i
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) V' U" h0 _. s0 }1 bVan Veen采泥器照片集：% `" E' R, a W0 P: P
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| Van Veen采泥器
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| 打开状态的Van Veen采泥器4 p3 H2 ]$ _9 c4 M
| 关闭状态的Van Veen采泥器
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1 S% h; J: m* s" n; S+ q- K2 T. j4.J. Gandraß Dipl.-Ing., M. Zoll,1996.Chlorinated Hydrocarbons in Sediments of the Elbe Catchment Area – Analytical Methods and Status of Pollution.Acta hydrochimica et hydrobiologica.24(5):212–217.3 P; o) q( v/ l: i% `0 N
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+ M V. A9 `2 `2 L: f8 W6.Catalina Castell Perez, Suzanne Roy, Maurice Levasseur, Donald M. Anderson,1998.CONTROL OF GERMINATION OF ALEXANDRIUM TAMARENSE (DINOPHYCEAE) CYSTS FROM THE LOWER ST. LAWRENCE ESTUARY (CANADA).Journal of Phycology.34(2):242–249.
, M6 f* W! B4 l% \$ ]7.A.V Tkalin, E.L Chaykovskaya,2000.Anthropogenic radionuclides in Peter the Great bay.Journal of Environmental Radioactivity.51(2):229–238.
' ?* ~% A% ^$ Q8.A. Tewari, H.V. Joshi, R.H. Trivedi, V.G. Sravankumar, C. Raghunathan, Y. Khambhaty, O.S. Kotiwar, S.K. Mandal,2001.The Effect of Ship Scrapping Industry and its Associated Wastes on the Biomass Production and Biodiversity of Biota in in situ Condition at Alang.Marine Pollution Bulletin.42(6):461–468.
8 M2 L _4 l# U- H9.DUQUESNE Sabine, LIESS Matthias ,2003.Increased sensitivity of the macroinvertebrate Paramorea walkeri to heavy-metal contamination in the presence of solar UV radiation in Antarctic shoreline waters.Marine ecology. Progress series.255:183-191.
7 f t8 f0 y+ g: `; t( P10.Pablo A. Lara-Martín, Abelardo Gómez-Parra, Eduardo González-Mazo,2005.Determination and distribution of alkyl ethoxysulfates and linear alkylbenzene sulfonates in coastal marine sediments from the Bay of Cadiz (southwest of Spain).Environmental Toxicology and Chemistry.24(9):2196–2202.
- x U" k8 l% I7 v) }! B11.A. Baeta, H.N. Cabral, J.M. Neto, J.C. Marques, M.A. Pardal,2005.Biology, population dynamics and secondary production of the green crab Carcinus maenas (L.) in a temperate estuary.Estuarine, Coastal and Shelf Science.65(1–2):43–52.
5 f' B1 h7 `: V7 s# P! P12.James E. Saunders, Khalid Mohammed Al Zahed, David M. Paterson,2007.The impact of organic pollution on the macrobenthic fauna of Dubai Creek (UAE).Marine Pollution Bulletin.54(11):1715–1723.
) T0 p) c v2 o* g1 A13.Ilona Hauser, Wolfgang Oschmann and Eberhard Gischler,2007.Taphonomic Signatures On Modern Caribbean Bivalve Shells As Indicators Of Environmental Conditions (Belize, Central America).Society for Sedimentary Geology."doi: 10.2110/palo.2007.p07-075r! `5 r" A7 I4 L& e
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15.Zengjie Jiang, Jianguang Fang, Guanhua Wang and Yuze Mao,2012.Identification of Aquaculture-Derived Organic Matter in the Sediment Associated with Coastal Fish Farming by Stable Carbon and Nitrogen Isotopes.Journal of Environmental Science and Engineering.A 1 (2012) 142-149.) S$ J0 k1 U' K- n' {. N
16.Claudia Propp, Ingo Jänen, Tim Jennerjahn,2013.Sources and Degradation of Sedimentary Organic Matter in Coastal Waters off the Brantas River, Java, Indonesia.Asian Journal of Water, Environment and Pollution.10(1):95-115.; A& Q6 {$ N: D9 |
17.Fazel Abdolahpur Monikh, Ammar Maryamabadi, Ahmad Savari, Kamal Ghanemi,2013.Heavy metals’ concentration in sediment, shrimp and two fish species from the northwest Persian Gulf.Toxicol Ind Health.doi: 10.1177/0748233713475498.2 L) X% q5 V3 Y1 Y1 P9 B8 P. i) r
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更多关键词：采泥器，静力采泥器，Day采泥器，底泥取样器，软质底泥采样器，抓泥斗，河流采样器，蚌式采泥器，彼得生采泥器，Van Veen采泥器，挖斗式采泥器，抓斗式采泥器" J, a: R0 g! i: C
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